Literature DB >> 33262346

The importance of sharing global forest data in a world of crises.

Jingjing Liang1, Javier G P Gamarra2.   

Abstract

Entities:  

Year:  2020        PMID: 33262346      PMCID: PMC7708831          DOI: 10.1038/s41597-020-00766-x

Source DB:  PubMed          Journal:  Sci Data        ISSN: 2052-4463            Impact factor:   6.444


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Amid ongoing global crises related to climate change, environmental degradation, pandemics, poverty, peace and justice, the international community has established 17 Sustainable Development Goals (SDG) as a roadmap to navigate the humanity through these uncharted waters. In parallel, signatories of the Paris agreement are committed to climate action through their Nationally Determined Contributions[1]. Although SDGs and Paris agreement pledges are complementary, the common roadmap of implementation is underperforming. New, unexpected global crises emerge almost every year from a lack of stewardship to stem the biosphere’s degradation[2]. Forest ecosystems are a critical node in an integrated systems approach to tackling global crises and achieving SDGs. Specifically, forest ecosystems provide crucial services such as absorbing 30% of anthropogenic greenhouse gas emissions[3], producing wood fuel or charcoal to 2.4 billion people[4], and being the most important global repository of terrestrial biodiversity, with 10% of its global area dedicated to biodiversity conservation[5]. Forest ecosystems sustain food, water and energy security, and human well-being[6], but deforestation and forest degradation are destroying a massive amount of forests worldwide, rendering more than 40,000 tropical tree species at risk[7]. Central to saving the world’s forest ecosystems, forest data enable the quantification of deforestation and forest degradation[5], and facilitate research into effective protection and conservation measures. Open access policies, as well as the development of supportive cyberinfrastructures, are key to meet an increasing public demand for forest information[8] for research, monitoring, policy-making, and other purposes. Over the past decades, users of forest data have expanded from a small group of authorized forestry researchers, government officials and private sector experts to all in the public domain who can benefit from this information. These data are now used by citizen scientists, environmentalists, and researchers from disciplines such as ecology, Earth sciences, and biological conservation. The quantity and quality of open forest data, however, still remains limited, especially in the tropics and other regions of the Global South (Fig. 1).
Fig. 1

Open in situ forest data are critical for the monitoring and mitigation of deforestation, forest degradation, biodiversity loss, and climate change (a), but sampling density of in situ forest data across the world, in number of sample plots per 1000 square kilometers, is generally low (b). Sampling density was calculated at the ecoregion[25] level, based a global database compiled by the Global Forest Biodiversity Initiative (GFBI, https://www.gfbinitiative.org/). Containing approx. 1.3 million sample plots, GFBI is one of the largest in situ forest datasets.

Open in situ forest data are critical for the monitoring and mitigation of deforestation, forest degradation, biodiversity loss, and climate change (a), but sampling density of in situ forest data across the world, in number of sample plots per 1000 square kilometers, is generally low (b). Sampling density was calculated at the ecoregion[25] level, based a global database compiled by the Global Forest Biodiversity Initiative (GFBI, https://www.gfbinitiative.org/). Containing approx. 1.3 million sample plots, GFBI is one of the largest in situ forest datasets. Forest data represent information systematically collected via remote sensing and ground (in situ) measurements for quantifying the status of a forest, including its ecological and economics conditions. While data from government-owned satellites and other remote sensing observations are increasingly being openly shared[9], the sharing of in situ forest data is still very limited. In situ forest data, similar to many other land-based sector data, originate from area-based sampling frame surveys. Three attributes are commonly measured and recorded in most in situ forest data—tree status (e.g. live, dead, recruitment, etc.), species, and diameter at breast height (dbh). Sometimes, other attributes can be taken at the same time, such as tree height and timber quality. Based on these elemental attributes, one can derive basal area, species diversity, site index, stand volume, and other metrics to quantify the status of a forest. Due to limitations in budget and labor, in situ forest data typically present relatively low sampling intensities over loosely defined tree target populations that are a priori unquantifiable. For example, regions with the highest sampling densities in the world encompass around three sample plots per one square kilometer of forested area, while for most of the world’s forested areas, the sampling density is less than one plot per 100 square kilometers (Fig. 1b). Here, we discuss the importance of sharing global forest data, especially in situ records, and outline major obstacles to sharing these data, as well as ongoing efforts and potential solutions to overcome them.

Forest Ecosystems in Crisis

Climate change, biodiversity loss, as well as deforestation and forest degradation, interconnected through potential positive feedbacks (e.g.[10]), are the three major crises collectively affecting forests worldwide. Climate influences the structure and function of forest ecosystems and plays an essential role in forest health. A changing climate may worsen many of the threats to forests, such as extreme weather damage, pest outbreaks, fires, human development, and drought[11]. A changing climate directly and indirectly affects the growth and productivity of forests, and alters the growing conditions, rendering some local tree species at risk if conditions in their current geographic ranges are no longer suitable. Meanwhile, climate change is found to increase the risk of drought in some areas and the risk of extreme precipitation and flooding in others[12]. The combined drought and extreme weather events increase wildfire risk, and hamper trees’ ability to protect themselves from insect pests. Under climate change, our planet’s biodiversity is undergoing an accelerated loss. From tropical rainforest to arctic tundra, substantial biodiversity loss at a global scale is undermining global terrestrial ecosystems at an alarming rate[6]. The role of biodiversity in the functioning of forest ecosystems has been under intensive investigation for the past two decades, and mounting evidence has shown that forest ecosystem function and productivity is affected by the loss of biodiversity[13]. To this end, biodiversity conservation is considered at least as important to achieving SDGs as the efforts to mitigate global climate change[6], and the two missions are closely connected and complementary. Ecosystems with greater biodiversity are better equipped to cope with climate change, extreme weather events and the emergence of diseases. On the other hand, climate change mitigation, along with a reduction in over-exploitation of resources, habitat destruction, pollution and the spread of invasive species, is one of the most effective measures to conserve and promote biodiversity[6]. Deforestation and forest degradation—including land use change and forest fragmentation—are tightly linked to climate change and biodiversity loss, and increase the risks of infectious diseases[14]. Human settlements in degraded forests bring humans into close contact with new opportunistic animals, and animals that struggle to stay in isolated fragments of natural vegetation. This has increased direct or indirect exposure of humans to zoonoses—yellow fever, ebola and coronavirus among others—which often spill over from one species to another at the margins of forests[14]. In fragmented forests and associated forest edges, agricultural fields, and pastures, many wildlife species are likely to disappear as forests are cleared, while others that have been able to adapt may become more concentrated, further increasing the rate of infections. The protection of forests, particularly in the tropics, and conservation of wildlife are therefore important to keep infectious agents in check.

Importance of Forest Data

Since the advent of remote sensing technology, some forest attributes can be measured using airborne, spaceborne and ground-based sensors, but in situ data still remain an indispensable and irreplaceable source of information especially for quantifying biodiversity and ground-truthing remote sensing data. For instance, with existing remote sensing and image processing technologies, it is difficult to identify tree species in a mixed-species forest with precision[15], especially for tropical forests and species-rich temperate forests. To this end, in situ data remain the most reliable information for forest resources and tree biodiversity assessment and monitoring, and will likely remain so in the foreseeable future[16]. Furthermore, due to a lack of in situ data for ground-truthing, the accuracy of many remotely sensed map products remains unassessed[17], jeopardizing their applications in timber and carbon accounting, biodiversity research and conservation. Assessing and monitoring biodiversity—central to global biodiversity conservation—is restricted by data limitation[18]. To date, large-scale conservation efforts have relied heavily on presence-only species count information (e.g.[19]) inferred from expert opinions or sparse incidence data collected from ad hoc local studies[20]. As a result, species abundance information for the majority of forest communities across the world has been relatively scarce, despite the importance of such information for prioritizing biological conservation[21]. Assessing and monitoring biodiversity across the world’s forest ecosystems will provide much needed guidance for future forest conservation efforts and considerably improve our understanding of the drivers of biodiversity loss under global environmental change. Degradation of forest ecosystems is manifested in many different ways, including a reduction in their ecological properties (such as receded canopy cover and reduced biodiversity) and ecosystem services (such as lowered timber productivity/quality and impaired carbon sequestration capability), as well as a decline in their resilience to and recovery from disturbances[22]. In practice, the United Nations Framework Convention on Climate Change (UNFCCC), following recommendations from the Intergovernmental Panel on Climate Change (IPCC) strongly advises combined approaches of in situ inventory and remote sensing data when assessing forest degradation and associated changes in forest area and carbon stocks[23].

Sharing of in Situ Forest Data

The last 10 years have witnessed a substantial increase in transparent and credible sharing of in situ forest data, which has resulted in an upsurge in forest research (e.g.[3,7,13]) and monitoring[16] at a global scale. The amount of shared in situ forest data, however, does not seem to meet the urgency of our global crises. The Global Forest Biodiversity Initiative (GFBI) database is one of the largest in situ forest databases consisting of 1.3 million sample plots across the world. Based on this, the sampling density of in situ forest data is commonly more than 10 plots per 1,000 square km in developed countries, whereas the sampling density for the tropics and other regions of the Global South is largely less than one plot per 1,000 square km (Fig. 1). Such a stark difference—between one and three orders of magnitude, depending on the region—in forest data availability across various biomes poses a major issue for tropical regions which host the vast majority of biodiversity. Overall, less than 30% of in situ forest datasets are open access. A lack of motivation constitutes one of the greatest hurdles in open sharing of in situ forest data. Except for a few countries mandated by their domestic law to share the national forest inventory (NFI) data, most of the remaining countries are reluctant or sometimes opposed to open sharing of forest data. Reasons for this include institutional miscoordination, national security, privacy, and potential disadvantages in the international negotiation on climate change offsets[24]. A lack of government transparency in this area can result in corruption, misinformed decision-making, and difficulties in the enforcement of forest protection and conservation. Moreover, a lack of motivation to share data also applies to many non-government data owners, who are not motivated to share these data without clear benefits, because in situ forest inventory data are often associated with high logistic and labor costs, especially in the tropics and other regions of the Global South. Major efforts have been made to overcome this hurdle in open sharing of forest data. The Food and Agriculture Organization of the United Nations (FAO) has initiated an open data initiative as part of a project to increase transparency in the forest sector (CBIT-Forest, http://www.fao.org/in-action/boosting-transparency-forest-data/en/). The FAO recognizes both the national contexts of many countries and the increasing demands of international donors that support the development of NFIs in recipient countries. It aims to capitalize on its historical presence in these countries and on the recent growth in NFIs, many of which it directly supports. It will offer countries open data platforms and analysis tools, while helping to provide forest scientists worldwide with vast amounts of much-needed forest microdata from mostly tropical countries. Simultaneously, tremendous efforts have been made by non-government actors to compile in situ forest data and make them available to data users, including the Global Forest Biodiversity Initiative (GFBI), the Amazon Forest Inventory Network (RAINFOR), Global Biodiversity Information Facility (GBIF), the African Tropical Rainforest Observation Network (AfriTRON), and several other international research teams, networks, and initiatives.

Immediate Actions Needed

The open sharing of in situ forest data is directly affecting the public awareness, research, monitoring and policy making of forest resources worldwide. Consequently, our ability to mitigate climate change, biodiversity loss, as well as deforestation and forest degradation largely depends on it. While no single model has been successful in achieving the goal of open in situ forest data worldwide, an integration of top-down (such as FAO’s CBIT-Forest transparency initiative) and bottom-up (such as AfriTRON, GBIF, GFBI, RAINFOR) approaches has shown the most promising outcomes. To this end, a shared responsibility by governments, scientists, NGOs, indigenous people, and other forest monitoring groups, in both rich and poor nations, will be key to the success and sustainability of the open sharing of global forest data. Low-income countries in particular need supporting assurances with regard to data governance and sustainability. Clear legal alignments between institutions on data sharing agreements and licenses for redistribution, as well as alignments with open data international standards will provide a solid basis for data governance. Meanwhile, innovative funding mechanisms are needed to promote data sustainability for low-income countries. For example, forest inventories funded for reducing emissions from deforestation and forest degradation, and for promoting conservation, sustainable management of forests and enhancement of forest carbon stocks in developing countries (REDD + ), can be incorporated into existing forest monitoring systems. This type of innovative funding mechanisms - based on shared responsibility - will be critical to sustain the procurement of in situ forest data from low-income countries. This includes multiple purposes such as the management of forest resources, the mitigation of climate change, and the conservation of biodiversity. The severe shortage of experts and facilities poses another major hurdle for the collection of forest inventory data, especially in the tropics and other regions of the Global South where sampling density of in situ forest data is very low (Fig. 1). Proper education and capacity development of new generations of tree taxonomists, forest scientists and foresters will be critical to improve forest data coverage, while bringing tangible benefits to the local economy of rural communities around the world. Nevertheless, the urgency to fulfill the SDGs and protect forest ecosystems requires immediate worldwide attention to open forest data.
  14 in total

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Review 6.  The biodiversity of species and their rates of extinction, distribution, and protection.

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Journal:  Science       Date:  2014-05-30       Impact factor: 47.728

7.  Paris Agreement climate proposals need a boost to keep warming well below 2 °C.

Authors:  Joeri Rogelj; Michel den Elzen; Niklas Höhne; Taryn Fransen; Hanna Fekete; Harald Winkler; Roberto Schaeffer; Fu Sha; Keywan Riahi; Malte Meinshausen
Journal:  Nature       Date:  2016-06-30       Impact factor: 49.962

Review 8.  Navigating the unfolding open data landscape in ecology and evolution.

Authors:  Antica Culina; Miriam Baglioni; Tom W Crowther; Marcel E Visser; Saskia Woutersen-Windhouwer; Paolo Manghi
Journal:  Nat Ecol Evol       Date:  2018-02-16       Impact factor: 15.460

Review 9.  Automated plant species identification-Trends and future directions.

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Journal:  PLoS Comput Biol       Date:  2018-04-05       Impact factor: 4.475

10.  Estimating the global conservation status of more than 15,000 Amazonian tree species.

Authors:  Hans Ter Steege; Nigel C A Pitman; Timothy J Killeen; William F Laurance; Carlos A Peres; Juan Ernesto Guevara; Rafael P Salomão; Carolina V Castilho; Iêda Leão Amaral; Francisca Dionízia de Almeida Matos; Luiz de Souza Coelho; William E Magnusson; Oliver L Phillips; Diogenes de Andrade Lima Filho; Marcelo de Jesus Veiga Carim; Mariana Victória Irume; Maria Pires Martins; Jean-François Molino; Daniel Sabatier; Florian Wittmann; Dairon Cárdenas López; José Renan da Silva Guimarães; Abel Monteagudo Mendoza; Percy Núñez Vargas; Angelo Gilberto Manzatto; Neidiane Farias Costa Reis; John Terborgh; Katia Regina Casula; Juan Carlos Montero; Ted R Feldpausch; Euridice N Honorio Coronado; Alvaro Javier Duque Montoya; Charles Eugene Zartman; Bonifacio Mostacedo; Rodolfo Vasquez; Rafael L Assis; Marcelo Brilhante Medeiros; Marcelo Fragomeni Simon; Ana Andrade; José Luís Camargo; Susan G W Laurance; Henrique Eduardo Mendonça Nascimento; Beatriz S Marimon; Ben-Hur Marimon; Flávia Costa; Natalia Targhetta; Ima Célia Guimarães Vieira; Roel Brienen; Hernán Castellanos; Joost F Duivenvoorden; Hugo F Mogollón; Maria Teresa Fernandez Piedade; Gerardo A Aymard C; James A Comiskey; Gabriel Damasco; Nállarett Dávila; Roosevelt García-Villacorta; Pablo Roberto Stevenson Diaz; Alberto Vincentini; Thaise Emilio; Carolina Levis; Juliana Schietti; Priscila Souza; Alfonso Alonso; Francisco Dallmeier; Leandro Valle Ferreira; David Neill; Alejandro Araujo-Murakami; Luzmila Arroyo; Fernanda Antunes Carvalho; Fernanda Coelho Souza; Dário Dantas do Amaral; Rogerio Gribel; Bruno Garcia Luize; Marcelo Petrati Pansonato; Eduardo Venticinque; Paul Fine; Marisol Toledo; Chris Baraloto; Carlos Cerón; Julien Engel; Terry W Henkel; Eliana M Jimenez; Paul Maas; Maria Cristina Peñuela Mora; Pascal Petronelli; Juan David Cardenas Revilla; Marcos Silveira; Juliana Stropp; Raquel Thomas-Caesar; Tim R Baker; Doug Daly; Marcos Ríos Paredes; Naara Ferreira da Silva; Alfredo Fuentes; Peter Møller Jørgensen; Jochen Schöngart; Miles R Silman; Nicolás Castaño Arboleda; Bruno Barçante Ladvocat Cintra; Fernando Cornejo Valverde; Anthony Di Fiore; Juan Fernando Phillips; Tinde R van Andel; Patricio von Hildebrand; Edelcilio Marques Barbosa; Luiz Carlos de Matos Bonates; Deborah de Castro; Emanuelle de Sousa Farias; Therany Gonzales; Jean-Louis Guillaumet; Bruce Hoffman; Yadvinder Malhi; Ires Paula de Andrade Miranda; Adriana Prieto; Agustín Rudas; Ademir R Ruschell; Natalino Silva; César I A Vela; Vincent A Vos; Eglée L Zent; Stanford Zent; Angela Cano; Marcelo Trindade Nascimento; Alexandre A Oliveira; Hirma Ramirez-Angulo; José Ferreira Ramos; Rodrigo Sierra; Milton Tirado; Maria Natalia Umaña Medina; Geertje van der Heijden; Emilio Vilanova Torre; Corine Vriesendorp; Ophelia Wang; Kenneth R Young; Claudia Baider; Henrik Balslev; Natalia de Castro; William Farfan-Rios; Cid Ferreira; Casimiro Mendoza; Italo Mesones; Armando Torres-Lezama; Ligia Estela Urrego Giraldo; Daniel Villarroel; Roderick Zagt; Miguel N Alexiades; Karina Garcia-Cabrera; Lionel Hernandez; Isau Huamantupa-Chuquimaco; William Milliken; Walter Palacios Cuenca; Susamar Pansini; Daniela Pauletto; Freddy Ramirez Arevalo; Adeilza Felipe Sampaio; Elvis H Valderrama Sandoval; Luis Valenzuela Gamarra
Journal:  Sci Adv       Date:  2015-11-20       Impact factor: 14.136

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1.  Co-limitation towards lower latitudes shapes global forest diversity gradients.

Authors:  Jingjing Liang; Javier G P Gamarra; Nicolas Picard; Mo Zhou; Bryan Pijanowski; Douglass F Jacobs; Peter B Reich; Thomas W Crowther; Gert-Jan Nabuurs; Sergio de-Miguel; Jingyun Fang; Christopher W Woodall; Jens-Christian Svenning; Tommaso Jucker; Jean-Francois Bastin; Susan K Wiser; Ferry Slik; Bruno Hérault; Giorgio Alberti; Gunnar Keppel; Geerten M Hengeveld; Pierre L Ibisch; Carlos A Silva; Hans Ter Steege; Pablo L Peri; David A Coomes; Eric B Searle; Klaus von Gadow; Bogdan Jaroszewicz; Akane O Abbasi; Meinrad Abegg; Yves C Adou Yao; Jesús Aguirre-Gutiérrez; Angelica M Almeyda Zambrano; Jan Altman; Esteban Alvarez-Dávila; Juan Gabriel Álvarez-González; Luciana F Alves; Bienvenu H K Amani; Christian A Amani; Christian Ammer; Bhely Angoboy Ilondea; Clara Antón-Fernández; Valerio Avitabile; Gerardo A Aymard; Akomian F Azihou; Johan A Baard; Timothy R Baker; Radomir Balazy; Meredith L Bastian; Rodrigue Batumike; Marijn Bauters; Hans Beeckman; Nithanel Mikael Hendrik Benu; Robert Bitariho; Pascal Boeckx; Jan Bogaert; Frans Bongers; Olivier Bouriaud; Pedro H S Brancalion; Susanne Brandl; Francis Q Brearley; Jaime Briseno-Reyes; Eben N Broadbent; Helge Bruelheide; Erwin Bulte; Ann Christine Catlin; Roberto Cazzolla Gatti; Ricardo G César; Han Y H Chen; Chelsea Chisholm; Emil Cienciala; Gabriel D Colletta; José Javier Corral-Rivas; Anibal Cuchietti; Aida Cuni-Sanchez; Javid A Dar; Selvadurai Dayanandan; Thales de Haulleville; Mathieu Decuyper; Sylvain Delabye; Géraldine Derroire; Ben DeVries; John Diisi; Tran Van Do; Jiri Dolezal; Aurélie Dourdain; Graham P Durrheim; Nestor Laurier Engone Obiang; Corneille E N Ewango; Teresa J Eyre; Tom M Fayle; Lethicia Flavine N Feunang; Leena Finér; Markus Fischer; Jonas Fridman; Lorenzo Frizzera; André L de Gasper; Damiano Gianelle; Henry B Glick; Maria Socorro Gonzalez-Elizondo; Lev Gorenstein; Richard Habonayo; Olivier J Hardy; David J Harris; Andrew Hector; Andreas Hemp; Martin Herold; Annika Hillers; Wannes Hubau; Thomas Ibanez; Nobuo Imai; Gerard Imani; Andrzej M Jagodzinski; Stepan Janecek; Vivian Kvist Johannsen; Carlos A Joly; Blaise Jumbam; Banoho L P R Kabelong; Goytom Abraha Kahsay; Viktor Karminov; Kuswata Kartawinata; Justin N Kassi; Elizabeth Kearsley; Deborah K Kennard; Sebastian Kepfer-Rojas; Mohammed Latif Khan; John N Kigomo; Hyun Seok Kim; Carine Klauberg; Yannick Klomberg; Henn Korjus; Subashree Kothandaraman; Florian Kraxner; Amit Kumar; Relawan Kuswandi; Mait Lang; Michael J Lawes; Rodrigo V Leite; Geoffrey Lentner; Simon L Lewis; Moses B Libalah; Janvier Lisingo; Pablito Marcelo López-Serrano; Huicui Lu; Natalia V Lukina; Anne Mette Lykke; Vincent Maicher; Brian S Maitner; Eric Marcon; Andrew R Marshall; Emanuel H Martin; Olga Martynenko; Faustin M Mbayu; Musingo T E Mbuvi; Jorge A Meave; Cory Merow; Stanislaw Miscicki; Vanessa S Moreno; Albert Morera; Sharif A Mukul; Jörg C Müller; Agustinus Murdjoko; Maria Guadalupe Nava-Miranda; Litonga Elias Ndive; Victor J Neldner; Radovan V Nevenic; Louis N Nforbelie; Michael L Ngoh; Anny E N'Guessan; Michael R Ngugi; Alain S K Ngute; Emile Narcisse N Njila; Melanie C Nyako; Thomas O Ochuodho; Jacek Oleksyn; Alain Paquette; Elena I Parfenova; Minjee Park; Marc Parren; Narayanaswamy Parthasarathy; Sebastian Pfautsch; Oliver L Phillips; Maria T F Piedade; Daniel Piotto; Martina Pollastrini; Lourens Poorter; John R Poulsen; Axel Dalberg Poulsen; Hans Pretzsch; Mirco Rodeghiero; Samir G Rolim; Francesco Rovero; Ervan Rutishauser; Khosro Sagheb-Talebi; Purabi Saikia; Moses Nsanyi Sainge; Christian Salas-Eljatib; Antonello Salis; Peter Schall; Dmitry Schepaschenko; Michael Scherer-Lorenzen; Bernhard Schmid; Jochen Schöngart; Vladimír Šebeň; Giacomo Sellan; Federico Selvi; Josep M Serra-Diaz; Douglas Sheil; Anatoly Z Shvidenko; Plinio Sist; Alexandre F Souza; Krzysztof J Stereńczak; Martin J P Sullivan; Somaiah Sundarapandian; Miroslav Svoboda; Mike D Swaine; Natalia Targhetta; Nadja Tchebakova; Liam A Trethowan; Robert Tropek; John Tshibamba Mukendi; Peter Mbanda Umunay; Vladimir A Usoltsev; Gaia Vaglio Laurin; Riccardo Valentini; Fernando Valladares; Fons van der Plas; Daniel José Vega-Nieva; Hans Verbeeck; Helder Viana; Alexander C Vibrans; Simone A Vieira; Jason Vleminckx; Catherine E Waite; Hua-Feng Wang; Eric Katembo Wasingya; Chemuku Wekesa; Bertil Westerlund; Florian Wittmann; Verginia Wortel; Tomasz Zawiła-Niedźwiecki; Chunyu Zhang; Xiuhai Zhao; Jun Zhu; Xiao Zhu; Zhi-Xin Zhu; Irie C Zo-Bi; Cang Hui
Journal:  Nat Ecol Evol       Date:  2022-08-08       Impact factor: 19.100

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